Heavy metal concentration in the moss Pleurozium schreberi in the Niepołomice Forest,Poland: changes during 20 years

The Niepo0">omice Forest is a large forestcomplex (110 km²) situated in southern Poland 10 to 30 kmto the east of the urban industrial Kraków agglomeration andsteelworks, which was built up on the outskirts of the city in1950. Due to prevailing westerly winds, the forest is affectedby pollutants emitted by both the steelworks and the city. Thelevel of heavy metal contamination in the Niepo0">omice Forestwas described using a sensitive bioindicator 013; the moss Pleurozium schreberi. Mean concentrations of metals in mosscollected in the Niepo0">omice Forest were Cd 013; 0.71, Cr 013; 2.4,Cu 013; 8.6, Fe 013; 673, Pb 013; 12.7, and Zn 013; 61 mg/kg.Concentrations of heavy metals in moss in the Niepo0">omiceForest decreased in time. As compared with the relatively cleanarea in north-eastern Poland (Puszcza Bia0">owieska), the concentration of Fe was 2013;9 fold and Pb 4013;6 fold higher in theNiepo0">omice Forest in 1975, while in 1998 4 fold and 2 fold,respectively. In both 1975 and 1998 the most polluted by heavymetals was the western part of the Niepo0">omice Forest (closestto the pollution sources) and the area along the roads insidethe forest complex.     

The Quality of Water in the Buško Blato Reservoir

The article presents the results of chemical andmicrobiological measurements of the water quality in theBu0">ko Blato reservoir, the largest in Europe, in the period 1989 to 1998.The aim was to observe possiblechanges in water quality during the past decade and itsinfluence on the downstream section of the Cetina River andits numerous tributaries and reservoirs, where there are twolarge regional water supply systems. This reservoir wasbuilt in order to exploit the high hydro-electric potentialof small streamflows in the karst fields of south-westernBosnia. It has strongly influenced the hydrologicconditions of the downstream section of the Cetina River.Bu0">ko Blato is a relatively shallow reservoir with the meandepth of 5 m. It covers an area of 57 km². The waterexchange in the reservoir is slow, occurring from one toseveral years. When the water inflow exceeds the hydroelectric plant demands the excess water is delivered by a reversible channel and pre-pumped into the Bu0">ko Blato reservoir. The total and carbonate water hardness in thereservoir is lower than in the Cetina River and in typicalkarst streamflows, since the water in this reservoir comesmainly from surface sources including numerous springs withhigh capacity oscillations, torrents and rainfall.Measurements, carried out during the past years, showed asignificant increase in nitrate content as well as in thecoli bacteria and a less significant increase in totalphosphorus content. The water quality was evaluated asmezotrophic according to the total phosphorus content basedon the Carlson index of trophic level, a lower quality thanin the Peru0">a reservoir, upstream on the Cetina River. Thelatter contains a smaller phosphorus content and wasclassed between oligotrophic and mezotrophic. According tothese data, employing the Vollenweider equation, the totalphosphorus content in this water should not exceed the meanof 20 mg m^-3 P. The results indicate that the water inthe Bu0">ko Blato reservoir did not deteriorate the waterquality on the downstream section of the Cetina River.     

Degradation of poly(β-hydroxyalkanoates) and polyolefin blends in a municipal wastewater treatment facility

Six types of plastics and plastic blends, the latter composed at least partially of biodegradable material, were exposed to aerobically treated wastewater (activated sludge) to ascertain their biodegradability. In one study, duplicate samples of 6% starch in polypropylene, 12% starch in linear low-density polyethylene, 30% polycaprolactone in linear low-density polyethylene, and poly(04q6v5n0m722170/xxlarge946.gif" alt="beta" align="MIDDLE" BORDER="0">-hydroxybutyrate-co-hydroxyvalerate) (PHB/V), a microbially produced polyester, were exposed to activated sludge for 5 months, and changes in mass, molecular weight average, and tensile properties were measured. None of the blended material showed any sign of degradation. PHB/V, however, showed a considerable loss of mass and a significant loss of tensile strength. In a second study, PHB/V degraded rapidly, but another type of microbial polymer which forms a thermoplastic elastomer, poly(04q6v5n0m722170/xxlarge946.gif" alt="beta" align="MIDDLE" BORDER="0">-hydroxyoctanoate), did not degrade. These results illustrate the potential for disposal and degradation of PHB/V in municipal wastewater.     

全球能源消费与CO2排放量

在收集全球能源储量和流通状况的基础上，综述了世界各地区能源消费量和各国人均能源水平，汇总了全球ＣＯ２排放总量及各大洲对全球ＣＯ２排放量的贡献率，到２１００年，全球Ｃ矿量预计将从目前６０亿ｔ／ａ增加到３６０亿ｔ／ａ，同时，旨出１９９６年中世界人口１８．８％的北美、欧洲、日本、ＣＯ２排放３１．６亿ｔ（碳），占全球当年ＣＯ２排放总量的５２．４％。     

南京夏季大气臭氧光化学特征与敏感性分析

对流层臭氧（O₃）主要由氮氧化物（NO_x）和挥发性有机物（VOCs）经过一系列光化学反应生成,反应过程呈现复杂的非线性关系.为深入了解O₃的光化学特征及生成机制,利用2018年夏季大气O₃与VOCs的观测数据,结合大气零维框架模拟模型F0AM-MCM,研究O₃超标日和非O₃超标日的O₃光化学特征之间的差异性.观测结果表明,O₃超标日期间φ（O₃）和φ（TVOCs）的平均值分别为47.8×10^-9和49.0×10^-9,为非O₃超标日期间O₃（26×10^-9）和TVOCs（30×10^-9）体积分数的1.8倍和1.6倍.使用F0AM模型,借助EKMA曲线和RIR分析等识别O₃敏感性,发现南京市O₃超标日和非O₃超标日O₃的形成均主要受VOCs和NO_x的协同控制.F0AM-MCM模拟结果表明,在O₃超标日,·OH和HO₂的日平均混合比分别是非O₃超标日的1.3倍和1.8倍,表明O₃超标日期间具有更强的大气氧化能力,且·OH和HO₂的形成和损失速率也有明显的增加,表明自由基循环的增强.此外,O₃超标日的O₃生成速率明显高于非O₃超标日,从而导致了O₃超标日的O₃净生成速率明显高于非O₃超标日.以上发现提高了对南京夏季O₃超标日大气O₃光化学特征的认识.     

基于国内外灾害经济研究与管理实践的启示

中外学者从不同视域对灾害经济与管理问题进行了研究,形成了一些有代表性的观点。各国政府在防灾减灾、灾后重建等方面也积累了大量的经验。这些观点和经验为我们深入研究灾害管理机制奠定了基础,结合汶川8.0级地震导致的惨重损失及灾后重建出现的问题,阐述了构建我国以人为本的灾害管理机制和可持续重建地震灾区的基本对策。     

新《防震减灾法》浅议——以汶川8.0级地震为例

以汶川8.0级地震为例,对新《防震减灾法》进行了解读,新《防震减灾法》在旧法的基础上,主要完善了防震减灾规划制度、建设工程抗震设防制度,增加了对学校医院等重要建筑和农村民居、乡村公共设施的抗震设防要求的规定,强化了防震减灾群测群防制度以加强对地震灾害的预防;完善了地震应急救援机制;进一步规范了地震灾后过渡性安置和恢复重建制度;加强了政府在防震减灾工作中的领导和协调作用。同时文中也指出了新《防震减灾法》存在的不足。     

Global energy and emissions scenarios for effective climate change mitigation—Deterministic and stochastic scenarios with the TIAM model

The achievement possibilities of the EU 2 0;C climate target have been assessed with the ETSAP TIAM global energy systems model. Cost-effective global and regional mitigation scenarios of carbon dioxide, methane, nitrous oxide and F-gases were calculated with alternative assumptions on emissions trading. In the mitigation scenarios, an 85% reduction in CO₂ emissions is needed from the baseline, and very significant changes in the energy system towards emission-free sources take place during this century. The largest new technology groups are carbon-capture and storage (CCS), nuclear power, wind power, advanced bioenergy technologies and energy efficiency measures. CCS technologies contributed a 5.5-Pg CO₂ annual emission reduction by 2050 and 12 Pg CO₂ reduction by 2100. Also large-scale forestation measures were found cost-efficient. Forestation measures reached their maximum impact of 7.7 Pg CO₂ annual emission reduction in 2080. The effects of uncertainties in the climate sensitivity have been analysed with stochastic scenarios.     

附加环境因素:传统比较优势理论的扩展

在李嘉圈模型中，若将环境成本用追加的劳动投入来衡量。可以发现，环境成本的引入将修正传统的比较优势格局。在H-O模型中耐加环境因素，亦即假定环境作为一种生产要搴而起作用。则所形成的比较优势将建立在包含环境要素真实价格的基础之上。本文最后指出，环境要素的真实价格与现实价格的脱离，使“显示的比较优势”有可能与真实的比较优势发生偏离。从而损害效率与公平。     

Time discounting and the decision to protect areas that are near and threatened or remote and cheap to acquire

Should conservation organizations focus on protecting habitats that are at imminent risk of being converted but are expensive or more remote areas that are less immediately threatened but where a large amount of land can be set aside? Variants of this trade‐off commonly arise in spatial planning. I used models of land‐use change near a deforestation frontier to examine this trade‐off. The optimal choice of where to protect was determined by how decisions taken today accounted for ecological benefits and economic costs of conservation actions that would occur sometime in the future. I used an ecological and economic discount rate to weight these benefits and costs. A large economic discount rate favored protecting more remote areas, whereas a large, positive ecological discount rate favored protecting habitat near the current deforestation frontier. The decision over where to protect was also affected by the influence economic factors had on landowners' decisions, the rate of technological change, and ecological heterogeneity of the landscape. How benefits and costs through time are accounted for warrants careful consideration when specifying conservation objectives. It may provide a niche axis along which conservation organizations differentiate themselves when competing for donor funding or other support.